CN110104845A - A kind of percolation liquid membrane processing method reducing concentration output of fluid - Google Patents

A kind of percolation liquid membrane processing method reducing concentration output of fluid Download PDF

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Publication number
CN110104845A
CN110104845A CN201910502386.9A CN201910502386A CN110104845A CN 110104845 A CN110104845 A CN 110104845A CN 201910502386 A CN201910502386 A CN 201910502386A CN 110104845 A CN110104845 A CN 110104845A
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water
ultrafiltration
reaction
fenton
nanofiltration
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Inventor
袁洪涛
刘万鹏
方生龙
丁鹏
李聪
孔维鹏
胡永辉
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Wuhan Shenneng Environmental Protection Xingou Waste Power Generation Co Ltd
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Wuhan Shenneng Environmental Protection Xingou Waste Power Generation Co Ltd
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Priority to CN201910502386.9A priority Critical patent/CN110104845A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/442Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by nanofiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/06Contaminated groundwater or leachate
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The present invention relates to the percolation liquid membrane processing methods that one kind can reduce concentration output of fluid comprising following steps: S1. produces in water addition salt acid for adjusting pH value to meeting Fenton's reaction requirement to ultrafiltration that ultrafiltration water producing tank is collected into;S2. it is produced in the ultrafiltration after Fenton's reaction Chi Zhongxiang mixes up pH and adds hydrogen peroxide and ferrous sulfate in water, carry out Fenton's reaction, the COD for making ultrafiltration produce water is reduced to setting value or less;S3. addition reducing agent, subsequently into filtration treatment in plate-type hyperfiltration device, produces water and enters intermediate water pot storage to remove the fragrant remaining oxidizing species of reaction, after having nanofiltration system starting liquid level, starting nanofiltration system progress nanofiltration processing can qualified discharge after nanofiltration production water pH pulls back to middle life.Advantage is, by Fenton's reaction and plate-type hyperfiltration, treated produces water, can reach discharge standard after nanofiltration system, to eliminate next stage reverse osmosis membrane processing process, the yield of concentrate is greatly reduced and greatly reduce cost of investment.

Description

A kind of percolation liquid membrane processing method reducing concentration output of fluid
Technical field
The invention belongs to the rubbish percolation liquid membrane process fields of garbage incinerating power plant, and in particular to one kind can reduce concentration The percolation liquid membrane processing method of output of fluid.
Background technique
As the requirement that country administers environmental protection industry (epi) and water pollution is higher and higher, consumer waste infiltration liquid handles work Skill is gradually increased with drainage requirement, and domestic rubbish disposal standard of drainage mainly has " household refuse landfill sites contamination control mark at present It is quasi- " (GB16889-2008) and " integrated wastewater discharge standard " (GB8978-1996) two class, to meet above-mentioned two category Standard, percolate prevailing technology is all made of ultrafiltration, nanofiltration and reverse osmosis membrane separation advanced treatment process at present, by ultrafiltration, receives Water outlet after filter, reverse osmosis membrane group technology fully meets and is better than above-mentioned two class standard, and film advanced treatment process is with its maintenance Simplicity, stable effluent quality, processing cost is cheap and has the larger market advantage.But because of above-mentioned nanofiltration, reverse osmosis membrane depth Science and engineering skill, principle are to be filtered the macromolecular substances such as salinity and organic pollutant by the way of physics screening Screening, salinity and organic pollutant are there is no degrading and reducing, the only process of pollutant concentration and separation, thus sieve and Filtered clear liquid water stabilization is up to standard, and then to become pollutant concentration higher for salinity and organic pollutant through retaining, more Intractable concentrate.The common processing mode of garbage burning factory is then that spray system is utilized back to return the consumption of spray burner hearth, lime at present Pulping system is starched using consumption, but since its yield is larger, refuse thermal value low garbage burning factory in part can not completely consume, Then in order to solve the problems, such as concentrate, it has to sacrifice garbage power energy benefit, and increase concentrate and return discharge rate, to solve the hardly possible Topic.And household refuse landfill sites because without for return spray and the secondary appointed condition used, can only by recharge to landfill yard, but With the increase of landfill yard runing time, pollutant is not eliminated always, and continuous recharge leads to newly generated Sewage instead Dye object is constantly enriched with, and concentration constantly increases, and subsequent treatment process is caused to handle more difficult situation.Therefore the part by-product Processing and whereabouts, where the bottleneck for already becoming membrane treatment process or even percolate treating process, its by-product is subtracted Amount and processing have significance.
Summary of the invention
The present invention provides a kind of percolation liquid membrane processing method that can reduce concentration output of fluid, it is intended to reduce pollutant from source Concentration reduces film advanced treating process, reduces the yield of film concentrate, to solve garbage incinerating power plant concentration output of fluid mistake Greatly, can not it is completely internal consumption and caused by economic benefit reduce problem.
The technical scheme to solve the above technical problems is that at a kind of percolation liquid membrane that can reduce concentration output of fluid Reason method comprising following steps:
S1. addition salt acid for adjusting pH value is produced in water to meeting Fenton's reaction requirement to ultrafiltration that ultrafiltration water producing tank is collected into;
S2. it is produced in the ultrafiltration after Fenton's reaction Chi Zhongxiang mixes up pH and adds hydrogen peroxide and ferrous sulfate in water, carry out Fenton Reaction, the COD for making ultrafiltration produce water are reduced to setting value or less;
S3. it is remaining to remove fragrant reaction that the ultrafiltration after being reduced to setting value or less to COD value produces addition reducing agent in water Oxidizing species produce water and enter intermediate water pot storage, have nanofiltration system subsequently into filtration treatment in plate-type hyperfiltration device After starting liquid level, starting nanofiltration system carries out nanofiltration processing can row up to standard after nanofiltration production water pH is pulled back between 6.5-7.5 It puts.
Based on the above technical solution, the present invention can also do specific choice or optimal selection further below.
Preferably, salt acid for adjusting pH value is added in S1 meet Fenton's reaction requirement to 4.5-5.0.
It should be noted that the oxidisability of Fenton reagent is best between pH3~5, it is generally recognized that when pH is between 2-4 Reaction is best, but pH will pull back to neutrality when water qualified discharge, if Fenton's reaction is completed under the conditions of pH is lower, on the one hand Input amount a larger increase of hydrochloric acid, the usage amount of liquid alkaline also a larger increase, is unfavorable for cost when another aspect pH pulls back to neutrality It calculates, therefore the pH value of preferred Fenton's reaction is between 4.5-5.0 in the present invention.
Specifically, mixing up the ultrafiltration after pH to produce the COD of water is 500-600mg/L, it is preferred that the additive amount of hydrogen peroxide in S2 The mass ratio of COD content in water is produced as 1.2:1 with ultrafiltration, and the molar ratio of ferrous sulfate and hydrogen peroxide is 1:10.
Preferably, the setting value of COD described in S2 is 200mg/L.
Specifically, the reducing agent added in S3 is iron powder, zinc powder, frerrous chloride or ferrous sulfate, additive amount is with can The oxidation-reduction potential for making corresponding ultrafiltration produce water is down to subject to 150mV or less.
Specifically, the input amount of reducing agent is 10-20ppm.
Specifically, in S3 through plate-type hyperfiltration device treated produce water silt density index (SDI) below 5.
Compared with prior art, the beneficial effects of the present invention are:
Original mainstream membrane treatment process is that ultrafiltration, nanofiltration, reverse osmosis membrane are applied in combination, and the present invention is improved to surpass Filter, Fenton oxidation, plate-type hyperfiltration and nanofiltration combination, the combination of Fenton's reaction and plate-type hyperfiltration can direct rows up to standard after making nanofiltration It puts, saves original reverse osmosis membrane advanced treating process, the reverse osmosis concentrated liquid yield of system inflow 25% can be reduced, Greatly reduce the production burden of waste incineration production line;Fenton reactor is obviously low with total investment of plate-type hyperfiltration equipment In the equipment investment of former reverse osmosis membrane process, while maintenance cost is greatly reduced.
Detailed description of the invention
Fig. 1 is the process flow diagram of the percolation liquid membrane processing method provided by the invention for reducing concentration output of fluid.
Specific embodiment
Principles and features of the present invention are described below in conjunction with drawings and the specific embodiments, example is served only for solving The present invention is released, is not intended to limit the scope of the present invention.
As shown in Figure 1, the present invention provides a kind of percolation liquid membrane processing method that can reduce concentration output of fluid comprising as follows Step:
S1. addition salt acid for adjusting pH value is produced in water to meeting Fenton's reaction requirement to ultrafiltration that ultrafiltration water producing tank is collected into;
S2. it is produced in the ultrafiltration after Fenton's reaction Chi Zhongxiang mixes up pH and adds hydrogen peroxide and ferrous sulfate in water, carry out Fenton Reaction, the COD for making ultrafiltration produce water are reduced to setting value or less;
S3. it is remaining to remove fragrant reaction that the ultrafiltration after being reduced to setting value or less to COD value produces addition reducing agent in water Oxidizing species produce water and enter intermediate water pot storage, have nanofiltration system subsequently into filtration treatment in plate-type hyperfiltration device After starting liquid level, starting nanofiltration system carries out nanofiltration processing can row up to standard after nanofiltration production water pH is pulled back between 6.5-7.5 It puts.
Used method is then conventional method unless otherwise noted in following embodiment, if used drug is without spy It does not mentionlet alone bright, is commercial product.
Embodiment 1
A kind of percolation liquid membrane processing method reducing concentration output of fluid comprising following steps:
1) after ultrafiltration water producing tank collects ultrafiltration production water, according to ultrafiltration water yield and pH situation, salt acid for adjusting pH value is added extremely Between 4.5-5, enter subsequent processing after reaching the reaction condition of Fenton's reaction;
2) after Fenton's reaction pond receives ultrafiltration production water, ferrous sulfate and hydrogen peroxide stirring is added, wherein hydrogen peroxide adds The mass ratio of amount and ultrafiltration COD content is 1.2:1, and the dosage of ferrous sulfate is that the molar ratio of hydrogen peroxide dosage is 1:10, Ultrafiltration is produced into the COD in water by 500-600mg/L, degradation to 200mg/L or less;
3) larger oxidation will be generated, therefore to subsequent plate-type hyperfiltration membrane and nanofiltration system to ensure subsequent membrane module Service life, the reducing agent ferrous sulfate of 10-20ppm need to be added, oxidation-reduction potential is down to 150mv hereinafter, into plate Formula ultrafiltration apparatus.Mixed liquor after Fenton's reaction carries a large amount of suspended matters, if being directly entered nanofiltration membrane system at this time, will cause Nanofiltration membrane blocks rapidly.Therefore the part suspension enters plate-type hyperfiltration device, and after carrying out low energy consumption ultra-filtration filters, pollution refers to Number SDI≤5 reach nanofiltration membrane flow condition and enter next process, and the suspended matter being concentrated after filtered will form sludge, and need Mud discharging periodically is carried out to it, to guarantee plate-type hyperfiltration strainability;Production water enters intermediate water pot and carries out storage water storage, has After nanofiltration system starts liquid level, start nanofiltration system, the water outlet pH value of nanofiltration at this time is still maintained at 5 or so, need to add a small amount of liquid Sodium hydroxide carries out pH value and pulls back between 6.5-7.5, is detected the COD of the water outlet of nanofiltration at this time in 30mg/L or less and remaining is each Index is also all satisfied emission request.
Embodiment 2
A kind of percolation liquid membrane processing method reducing concentration output of fluid comprising following steps:
1) after ultrafiltration water producing tank collects ultrafiltration production water, according to ultrafiltration water yield and pH situation, salt acid for adjusting pH value is added extremely Between 3.5-4.5, enter subsequent processing after reaching the reaction condition of Fenton's reaction;
2) after Fenton's reaction pond receives ultrafiltration production water, ferrous sulfate and hydrogen peroxide stirring is added, wherein hydrogen peroxide adds The mass ratio of amount and ultrafiltration COD content is 1.3:1, and the dosage of ferrous sulfate is that the molar ratio of hydrogen peroxide dosage is 1:10, Ultrafiltration is produced into the COD in water by 500-600mg/L, degradation to 200mg/L or less;
3) larger oxidation will be generated, therefore to subsequent plate-type hyperfiltration membrane and nanofiltration system to ensure subsequent membrane module Service life, the reducing agent zinc powder of 10-20ppm need to be added, oxidation-reduction potential is down to 150mv hereinafter, into board-like super Filter device.Mixed liquor after Fenton's reaction carries a large amount of suspended matters, if being directly entered nanofiltration membrane system at this time, will cause nanofiltration Film blocks rapidly.Therefore the part suspension enters plate-type hyperfiltration device, after carrying out low energy consumption ultra-filtration filters, pollution index SDI≤5 reach nanofiltration membrane flow condition and enter next process, and the suspended matter being concentrated after filtered will form sludge, and need to determine Phase carries out mud discharging to it, to guarantee plate-type hyperfiltration strainability;Production water enters intermediate water pot and carries out storage water storage, has and receives After filter system starts liquid level, start nanofiltration system, the water outlet pH value of nanofiltration at this time is still maintained at 5 or so, need to add a small amount of liquid hydrogen Sodium oxide molybdena carry out pH value pull back between 6.5-7.5, through detected nanofiltration at this time water outlet COD 30mg/L or less and remaining respectively refer to Mark is also all satisfied emission request.
Embodiment 3
A kind of percolation liquid membrane processing method reducing concentration output of fluid comprising following steps:
1) after ultrafiltration water producing tank collects ultrafiltration production water, according to ultrafiltration water yield and pH situation, salt acid for adjusting pH value is added extremely Between 2.5-3.5, enter subsequent processing after reaching the reaction condition of Fenton's reaction;
2) after Fenton's reaction pond receives ultrafiltration production water, ferrous sulfate and hydrogen peroxide stirring is added, wherein hydrogen peroxide adds The mass ratio of amount and ultrafiltration COD content is 1.2:1, and the dosage of ferrous sulfate is that the molar ratio of hydrogen peroxide dosage is 1:10, Ultrafiltration is produced into the COD in water by 500-600mg/L, degradation to 200mg/L or less;
3) larger oxidation will be generated, therefore to subsequent plate-type hyperfiltration membrane and nanofiltration system to ensure subsequent membrane module Service life, the reducing agent iron powder of 10-20ppm need to be added, oxidation-reduction potential is down to 150mv hereinafter, into board-like super Filter device.Mixed liquor after Fenton's reaction carries a large amount of suspended matters, if being directly entered nanofiltration membrane system at this time, will cause nanofiltration Film blocks rapidly.Therefore the part suspension enters plate-type hyperfiltration device, after carrying out low energy consumption ultra-filtration filters, pollution index SDI≤5 reach nanofiltration membrane flow condition and enter next process, and the suspended matter being concentrated after filtered will form sludge, and need to determine Phase carries out mud discharging to it, to guarantee plate-type hyperfiltration strainability;Production water enters intermediate water pot and carries out storage water storage, has and receives After filter system starts liquid level, start nanofiltration system, the water outlet pH value of nanofiltration at this time is still maintained at 4 or so, need to add certain quantity of fluid Sodium hydroxide carries out pH value and pulls back between 6.5-7.5, is detected the COD of the water outlet of nanofiltration at this time in 30mg/L or less and remaining is each Index is also all satisfied emission request.
It should be noted that reaching emission request after nanofiltration processing in the various embodiments described above, without further using Reverse osmosis membrane processing, nanofiltration membrane system only generates the concentration liquid measure for being equivalent to inflow 15% at this time, handles according to original process, Continue to be further processed using reverse osmosis membrane into system after nanofiltration membrane system, then generation is also equivalent to inflow 25% Liquid measure is concentrated, namely the processing method provided through the invention carries out percolation liquid membrane processing, and the production of concentrate can be greatly lowered Amount.
The foregoing is merely presently preferred embodiments of the present invention, is not intended to limit the invention, it is all in spirit of the invention and Within principle, any modification, equivalent replacement, improvement and so on be should all be included in the protection scope of the present invention.

Claims (7)

1. the percolation liquid membrane processing method that one kind can reduce concentration output of fluid, which comprises the steps of:
S1. addition salt acid for adjusting pH value is produced in water to meeting Fenton's reaction requirement to ultrafiltration that ultrafiltration water producing tank is collected into;
S2. it is produced in the ultrafiltration after Fenton's reaction Chi Zhongxiang mixes up pH and adds hydrogen peroxide and ferrous sulfate in water, carry out Fenton's reaction, The COD for making ultrafiltration produce water is reduced to setting value or less;
S3. the ultrafiltration after being reduced to setting value or less to COD value, which produces, adds reducing agent to remove the fragrant remaining strong oxygen of reaction in water The property changed substance produces water and enters intermediate water pot storage, have nanofiltration system starting subsequently into filtration treatment in plate-type hyperfiltration device After liquid level, starting nanofiltration system carries out nanofiltration processing can qualified discharge after nanofiltration production water pH is pulled back between 6.5-7.5.
2. the percolation liquid membrane processing method that one kind according to claim 1 can reduce concentration output of fluid, which is characterized in that S1 Middle addition salt acid for adjusting pH value meets Fenton's reaction requirement to 4.5-5.0.
3. the percolation liquid membrane processing method that one kind according to claim 1 can reduce concentration output of fluid, which is characterized in that adjust The COD that ultrafiltration after good pH produces water is 500-600mg/L, and the additive amount of hydrogen peroxide and ultrafiltration produce the matter of COD content in water in S2 Ratio is measured as 1.2:1, the molar ratio of ferrous sulfate and hydrogen peroxide is 1:10.
4. the percolation liquid membrane processing method that one kind according to claim 1 can reduce concentration output of fluid, which is characterized in that S2 Described in COD setting value be 200mg/L.
5. the percolation liquid membrane processing method that one kind according to claim 1 can reduce concentration output of fluid, which is characterized in that S3 The reducing agent of middle addition is iron powder, zinc powder, frerrous chloride or ferrous sulfate, and additive amount is can make corresponding ultrafiltration produce water Oxidation-reduction potential is down to subject to 150mV or less.
6. the percolation liquid membrane processing method that one kind according to claim 5 can reduce concentration output of fluid, which is characterized in that also The input amount of former agent is 10-20ppm.
7. one kind according to any one of claims 1 to 6 can reduce the percolation liquid membrane processing method of concentration output of fluid, special Sign is, through plate-type hyperfiltration device, treated produces the silt density index (SDI) of water below 5 in S3.
CN201910502386.9A 2019-06-11 2019-06-11 A kind of percolation liquid membrane processing method reducing concentration output of fluid Pending CN110104845A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113292203A (en) * 2021-06-03 2021-08-24 广东雅迪环保设备有限公司 Method for removing white in landfill leachate

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102659270A (en) * 2012-05-14 2012-09-12 上海同济建设科技有限公司 Method for treating ultra-filtration water of garbage leachate
CN102976511A (en) * 2012-11-05 2013-03-20 开滦(集团)有限责任公司 Coking wastewater membrane filtration concentrate recycle method
CN105174524A (en) * 2014-06-09 2015-12-23 鞍钢股份有限公司 Pretreatment device and method before coking wastewater chemical oxygen demand detection
CN106219816A (en) * 2016-08-25 2016-12-14 万华化学集团股份有限公司 A kind of processing method of reverse osmosis concentrated water
CN108585381A (en) * 2018-06-07 2018-09-28 安徽德玉环境工程装备有限公司 A kind of brush waste water treatment system processed
CN109761416A (en) * 2019-03-07 2019-05-17 山东泰禾环保科技股份有限公司 Garbage leachate treatment process and its processing unit

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102659270A (en) * 2012-05-14 2012-09-12 上海同济建设科技有限公司 Method for treating ultra-filtration water of garbage leachate
CN102976511A (en) * 2012-11-05 2013-03-20 开滦(集团)有限责任公司 Coking wastewater membrane filtration concentrate recycle method
CN105174524A (en) * 2014-06-09 2015-12-23 鞍钢股份有限公司 Pretreatment device and method before coking wastewater chemical oxygen demand detection
CN106219816A (en) * 2016-08-25 2016-12-14 万华化学集团股份有限公司 A kind of processing method of reverse osmosis concentrated water
CN108585381A (en) * 2018-06-07 2018-09-28 安徽德玉环境工程装备有限公司 A kind of brush waste water treatment system processed
CN109761416A (en) * 2019-03-07 2019-05-17 山东泰禾环保科技股份有限公司 Garbage leachate treatment process and its processing unit

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
丁海燕: "《化工原理实验》", 31 July 2009, 青岛:中国海洋大学出版社 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113292203A (en) * 2021-06-03 2021-08-24 广东雅迪环保设备有限公司 Method for removing white in landfill leachate

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Application publication date: 20190809